Abstract

Nutrient-rich organic wastes and soil ameliorants can benefit crop performance and soil health but can also prevent crop nutrient sufficiency or increase greenhouse gas emissions. We hypothesised that nitrogen (N)-rich agricultural waste (poultry litter) amended with sorbents (bentonite clay or biochar) or compost (high C/N ratio) attenuates the concentration of inorganic nitrogen (N) in soil and reduces emissions of nitrous oxide (N2O). We tested this hypothesis with a field experiment conducted on a commercial sugarcane farm, using in vitro incubations. Treatments received 160 kg N ha−1, either from mineral fertiliser or poultry litter, with additional N (2–60 kg N ha−1) supplied by the sorbents and compost. Crop yield was similar in all N treatments, indicating N sufficiency, with the poultry litter + biochar treatment statistically matching the yield of the no-N control. Confirming our hypothesis, mineral N fertiliser resulted in the highest concentrations of soil inorganic N, followed by poultry litter and the amended poultry formulations. Reflecting the soil inorganic N concentrations, the average N2O emission factors ranked as per the following: mineral fertiliser 8.02% > poultry litter 6.77% > poultry litter + compost 6.75% > poultry litter + bentonite 5.5% > poultry litter + biochar 3.4%. All emission factors exceeded the IPCC Tier 1 default for managed soils (1%) and the Australian Government default for sugarcane soil (1.25%). Our findings reinforce concerns that current default emissions factors underestimate N2O emissions. The laboratory incubations broadly matched the field N2O emissions, indicating that in vitro testing is a cost-effective first step to guide the blending of organic wastes in a way that ensures N sufficiency for crops but minimises N losses. We conclude that suitable sorbent-waste formulations that attenuate N release will advance N efficiency and the circular nutrient economy.

Highlights

  • Sugarcane, a giant perennial C4 grass, is one of the fastest growing terrestrial plants and a major global commodity [1]

  • emission factors (EF) of 3.4 to 8.0 in our study mostly exceeded the average EF of 3.87 ± 1.16% calculated for sugarcane soils globally [6]

  • 0.04% to 6.7% from sugarcane fields fertilised with mineral N and managed with green cane harvesting [7,10,11,50,51,52], but were below the EF of 21% from Australian acid sulphate soil [8]

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Summary

Introduction

A giant perennial C4 grass, is one of the fastest growing terrestrial plants and a major global commodity [1]. A limitation to sustainable sugarcane production is its N footprint. Only 50% of N fertiliser is used by sugarcane crops, with as little as 10–30% in main producer countries [2]. Nitrogen losses from sugarcane soils occur via leaching and run-off [3,4], ammonia volatilisation [5] and nitrous oxide (N2 O). Emissions [6,7,8,9,10,11]. Nitrous oxide losses from agricultural soils are in the global spotlight, as they dominate the estimated 7.3 Tg N2 O-N of annual anthropogenic emissions [12].

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